Research Article - International Research Journal of Microbiology ( 2023) Volume 12, Issue 4
Received: 01-Jun-2023, Manuscript No. IRJM-23-100712; Editor assigned: 05-Jun-2023, Pre QC No. IRJM-23-100712 (PQ); Reviewed: 19-Jun-2023, QC No. IRJM-23-100712; Revised: 22-Jun-2023, Manuscript No. IRJM-23-100712 (R); Published: 24-Jul-2023, DOI: 10.14303/2141-5463.2023.46
Water, Sanitation, Hygiene, Environmental, Infrastructure, Diarrhoea
Diarrhoea is still a major disease burden in some parts of the globe, especially in Africa and other low and middleincome countries. The disease has been proven to be preventable and treatable. While deaths arising from this disease have reduced significantly, children from some low and middle-income countries still get sick. (Bakir et al., 2017) and WHO (2017) stated that about 525,000 annual deaths result from diarrhoea among children under five years of age. (Okun Da, 1999) reported that mortality attributable to diarrhoea is 10-fold higher in low-income countries than in industrialized countries. (WHO, 2017) posited that there are an estimated 1.7 billion cases of diarrhoea yearly with an average of 2.9 episodes per child. It is on record that about 9.9% of all under five-year deaths are attributable to diarrhoea. Some of the children die as a result of the disease while the surviving ones face long-term episodes of repeated infections and lasting impairments in addition to other challenges arising from COVID-19, climate change, antimicrobial resistance and issues associated with migration and urbanization (PATH, 2022). Some factors have been identified as precipitating the high prevalence of deaths due to diarrhoea. They include poor knowledge and attitude towards the disease, short supply of water and sanitation facilities, poverty, poor environmental hygiene, and poor personal hygiene. The deaths were attributable to poor sanitation, hygiene and unsafe drinking water put at 829,000 annually (WHO, 2019). Nigeria remains top of the ladder of countries still prone to cases of diarrhoea deaths among children at 51,810 per 100,000 people (PATH, 2017). In 2021 United Nations Inter-Agency Group for Mortality Estimation (UN IGME) observed that in 2017, while India recorded about 989,000 under-five deaths out of over 1 billion population, Nigeria recorded 714,000 under-five deaths out of about 200 million population. This under-five mortality rate estimate, according to UNIGME (2021), was 166 deaths per 1000 live births in 2003 and 114 deaths per 1000 live births in 2020. For our Abuja study area, it was 133 deaths per 1000 live births in 2003 and 106 deaths per 1000 live births in 2019 (UNIGME, 2021).
Amongst the necessities for the public’s good health is the availability of safe drinking (potable) water, which has to be readily accessible and of good quality (safely managed drinking water services), as contaminated water has been identified as the cause of several diseases. It is on record that an estimated 2 billion people globally have no access to safely managed sanitation services, safely managed water services and basic hand washing services (WHO, 2021). Several studies point to sanitation, family status and personal hygiene practices as other important factors contributing to diarrhoea prevalence and health burden (Hunachew B et al., 2018). WHO/UNICEF (2015) opined that poor sanitation is mostly found in rural settings and urban slums among vulnerable populations in low-income countries of South Asia, Southeast Asia and sub-Saharan Africa. (Sambe Ba et al., 2013) observed that in the past few decades, there has been an upsurge of a mass movement to the urban areas in sub-Saharan Africa and this has resulted in the springing up of urban slums. These slums are unplanned and have disorganised landscapes with most of their occupants living in crowded wretched conditions with inadequate safe water supply, drainage and sewerage systems, absence of/ inadequate sanitation and solid waste disposal/treatment systems. Hence, the increased risks of infectious diseases, respiratory infections and diarrhoea. Such slums exist in several cities in Nigeria. The available environmental infrastructure in these urban slums is frequently insufficient, inappropriate, and decrepit, with observed increases in health challenges. Thus, there appears to be a relationship between environmental infrastructure and health. It has been suggested that improving sanitation facilities and access to infrastructure can benefit public health. The Water, Sanitation and Hygiene (WASH) programme that captures interventions in these basic environmental infrastructure deficits has been adjudged a major integrated intervention effort for infectious disease prevention (WHO/UNICEF, 2021). However, toilet facility types and accessibility usually determine the degree of contact between humans and their excreta in the environment. It is noteworthy that most communities in developing countries share toilet facilities and as such, prevalence is affected by not only the type of available toilet structure but also the condition under which such toilets are used by the people. Water scarcity, which is common in most low-income countries, may bring about a decline in personal and hand hygiene habits since the hands are reservoirs of most pathogens.
Despite some knowledge of the risk factors associated with diarrhoea, there is still very limited literature on factors contributing to the prevalence of diarrhoea and the effects of provision or non-provision of these factors in several areas of Nigeria, including the Area Councils of Abuja, Nigeria. The lack of sufficient information on the diarrheal disease burden is detrimental to efficient and cost-effective planning of interventions against diarrhoea which is highly endemic in Nigeria (WHO, 2013). Recurring cholera (acute diarrhoea) and gastroenteritis outbreaks in some regions of Nigeria, including the Federal Capital Territory (FCT), are pointers to its sustained relevance as a disease of high public health importance. It also showed that no efforts should be spared until the diarrhoea scourge is permanently controlled. This study, thus, was designed to capture the available environmental infrastructure in suburban districts of Abuja, Nigeria and their contributions to diarrhoea occurrence in under five years old children.
Materials
The material used for this study was pre-tested structured questionnaires administered to mothers and child minders of the under fives.
Methods
Study area and population
The study was carried out in 2021 in two suburban districts (Abuja Municipal Area Council (AMAC) and Bwari Area Councils (BAC), of the Federal Capital Territory, Nigeria. Figure 1 is the map of the study area. AMAC lies within Latitudes 8o36’ and 9o21’ North of the Equator and Longitudes 7o07’ and 7o33’ East of Greenwich Meridian while Bwari Area Council is located between Latitude 6o45” and 7o45” North of the Equator and Longitude 8o25’ and 9o25’ East of the Greenwich Meridian (Balogun, 2001). AMAC has a projected population of about 776,298 and a land area of 1,476 km2 whilst BAC has a projected population of 229,274 and a land area of 938.744 km2 (Brinkoff, 2017). The study populations were mothers and childminders of children under five years of age who had diarrhoea in the two weeks preceding the survey and who gave their consent for the survey.
Administration of instrument of data and processing
A structured questionnaire was administered to mothers and childminders of under-five-year-olds in the study area totalling 399 and 398 for AMAC and BAC respectively.
This was achieved through random sampling using Taro Yamane sample size calculation. The illiterate participants were assisted in filling out the questionnaire. The filled questionnaires were analysed statistically using descriptive SPSS version 25. A return rate greater than 90% was achieved.
Results
The descriptive results of the data are presented in Tables 1 and 2. Table 3 shows the Chi-Square relationship between some socio-demographic and socio-economic factors and diarrhoea prevalence (Table 1-3).
AMAC | BAC | ||||
---|---|---|---|---|---|
Socio-Demographics | Options | Frequency | Percentage (%) | Frequency | Percentage (%) |
Age | ≤ 18 | 20 | 5 | 29 | 7.32 |
19-29 | 193 | 48.25 | 158 | 39.9 | |
30-41 | 160 | 40 | 136 | 34.34 | |
42-52 | 27 | 6.75 | 63 | 15.91 | |
≥53 | 0 | 0 | 10 | 2.53 | |
Sex | Male | 7 | 1.75 | 2 | 0.51 |
Female | 393 | 98.25 | 394 | 99.49 | |
Marital Status | Single | 35 | 8.75 | 32 | 8.08 |
Married | 329 | 82.25 | 277 | 69.95 | |
Widowed | 21 | 5.25 | 24 | 6.06 | |
Divorced | 14 | 3.5 | 39 | 9.85 | |
Separated | 1 | 0.25 | 24 | 6.06 | |
Occupation of Mother/ Childminder | Farmer | 24 | 6 | 98 | 24.75 |
Trader | 205 | 51.25 | 116 | 29.29 | |
Artisan | 17 | 4.25 | 1 | 0.25 | |
Stay at Home | 93 | 23.25 | 164 | 41.41 | |
Civil Servant | 61 | 15.25 | 17 | 4.29 | |
Educational Qualification | No Formal Education | 36 | 9 | 63 | 15.91 |
Primary | 29 | 7.25 | 137 | 34.6 | |
Secondary | 185 | 46.25 | 102 | 25.76 | |
Tertiary | 131 | 32.75 | 13 | 3.28 | |
School Drop-Out | 19 | 4.75 | 81 | 20.45 | |
Household size | 1 – 4 | 36 | 9 | 98 | 24.75 |
5 – 9 | 20 | 5 | 17 | 4.29 | |
10 – 14 | 204 | 51 | 117 | 29.55 | |
>14 | 140 | 35 | 164 | 41.41 | |
Household Wealth Quintile | Above N150,000 | 16 | 4 | 8 | 2 |
N100,000 – N150,000 | 27 | 6.75 | 25 | 6.25 | |
N50,000 – N 100,000 | 131 | 32.75 | 120 | 30 | |
Less than N 50,000 | 136 | 34 | 97 | 24.25 | |
No Income at all | 88 | 22 | 145 | 36.25 | |
Mother/Childminders diarrhoea knowledge | No knowledge | 81 | 20.25 | 81 | 20.45 |
Basic Knowledge | 190 | 47.5 | 189 | 47.73 | |
Very Knowledgeable | 2 | 0.5 | 2 | 0.5 | |
Not Sure | 103 | 25.75 | 103 | 26.01 | |
Indifferent | 20 | 5 | 81 | 20.45 | |
How Many Times Has Your Child Had Diarrhoea in the Past Two Weeks? | Not at all | 144 | 36 | 20 | 5.05 |
Once | 211 | 52.75 | 210 | 52.5 | |
2 Times | 35 | 8.75 | 35 | 8.75 | |
3 Times | 5 | 1.25 | 5 | 1.25 | |
More Than 3 Times | 0 | 0 | 20 | 5.05 | |
AMAC | BAC | |||
---|---|---|---|---|
Environmental Infrastructure | Frequency | Percentage (%) | Frequency | Percentage (%) |
Basic drinking water source | 173 | 43.36 | 0 | 0 |
Limited water source | 219 | 54.89 | 396 | 99.49 |
Return trip time <30 minutes | 335 | 83.96 | 272 | 68.34 |
Return trip time >30 minutes | 63 | 15.79 | 124 | 31.16 |
Hand wash with water only | 150 | 37.59 | 150 | 37.69 |
Hand wash with soap and water | 278 | 69.67 | 240 | 60.3 |
Right hand wash times | 350 | 87.72 | 371 | 93.22 |
Child’s stool disposal method (Improved) | 387 | 96.99 | 327 | 82.16 |
Child’s stool disposal method (Unimproved) | 12 | 3 | 69 | 17.34 |
Type of Toilet (Improved) | 365 | 91.48 | 306 | 76.88 |
Type of Toilet (Unimproved) | 33 | 8.27 | 90 | 22.61 |
Type of Toilet (Open Defecation) | 1 | 0.25 | 0 | 0 |
Toilet ownership (Private) | 290 | 72.68 | 183 | 45.98 |
Toilet Ownership (Shared) | 109 | 27.32 | 213 | 53.52 |
Variables |
Options | Frequency | Percent | X2 | df | p – value |
---|---|---|---|---|---|---|
For AMAC | ||||||
Occupation of Mother/Childminder | Farmer | 24 | 6 | 30.443a | 8 | 0 |
Trader | 205 | 51.25 | ||||
Artisan | 17 | 4.25 | ||||
Stay at Home | 93 | 23.25 | ||||
Civil Servant | 61 | 15.25 | ||||
Household Wealth Quintile | Above N150,000 | 16 | 4 | 28.962a | 8 | 0 |
N100,000 – N150,000 | 27 | 6.75 | ||||
N50,000 – N 100,000 | 131 | 32.75 | ||||
Less than N 50,000 | 136 | 34 | ||||
No Income at all | 88 | 22 | ||||
For BAC | ||||||
Occupation of Mother/Childminder | Farmer | 98 | 24.75 | 5.837a | 8 | 0.666 |
Trader | 116 | 29.29 | ||||
Artisan | 1 | 0.25 | ||||
Stay at Home | 164 | 41.41 | ||||
Civil Servant | 17 | 4.29 | ||||
Household Wealth Quintile | Above N150,000 | 8 | 2 | 5.197a | 8 | 0.736 |
N100,000 – N150,000 | 25 | 6.25 | ||||
N50,000 – N 100,000 | 120 | 30 | ||||
Less than N 50,000 | 97 | 24.25 | ||||
No Income at all | 145 | 36.25 |
Tables 4 and 5 are the Chi-Square results of the associations between the identified available infrastructure and diarrhoea prevalence in the study areas. In the two weeks preceding the survey of the 399 and 398 under-five study population, not less than 40 under-five children had diarrhoea at least twice. This gave an overall diarrhoea prevalence of 10% for both study areas. This is not far from the 15.1% recorded for FCT in 2018 by National Nutrition and Health Survey (Table 4 and 5).
Socio-demographic and socio-economic status of the participants
As shown in (Table 1), the participants in AMAC were mostly female (98.25%) and 82.25% of them were married while 88.25% were aged between 19 and 41 years. Their occupations included trading (51.25%), stay-at-home mothers (23.25%) and civil servants (15.25%). The survey showed that 9% of them had no formal education while 48% had a basic knowledge of diarrhoea while 20.25% had no knowledge at all. Most of the household sizes were above 10 in number (86%). For the wealth quintile of the households, the Table showed that 66.75% of the households thrived on NGN 50,000 to NGN 100,000 monthly, while 22% had no visible income. In BAC, the respondents were mostly female (99.49%) and 69.95% of them were married while 90.15% were aged between 19 and 52 years. Their occupations included trading (29.29%), stay-at-home mothers (41.41%) and farmers (24.75%). The Table showed that 15.91% of the participants had no formal education while 47.73% had a basic knowledge of diarrhoea while 20.45% had no knowledge at all. Household sizes of more than 14 were observed in 41.41% of the respondents while household sizes of less than 14 were observed in 58.59% of the respondents. For the wealth quintile of the households in BAC, the Table showed that 54.25% of the households thrived on less than NGN 50,000 to NGN100,000 monthly, while 36.25% had no visible income at all.
Available environmental infrastructure in the study area
From Table 2, in AMAC, improved and basic drinking water sources were available to 43.36% of the study population while 54.89% had improved and limited drinking water sources which were not safely managed. The water sources were not far from their homes based on the return trip time of mostly less than 30 minutes (83.96%) as stipulated by WHO. The hand hygiene practices of the participants were commendable as 87.72% claimed to practice the correct hand washing and 69.67% washed their hands correctly with soap and water while 37.59% washed with water only. Furthermore, Table 2 showed that in BAC, the study population had no access to basic drinking water sources that were improved and safely managed whereas 99.49% had improved and limited drinking water sources which were not safely managed. A less than 30-minute trip time was recorded for 68.34% of the respondents while 31.16% had a return trip time greater than 30 minutes. The hand hygiene practices of the participants were commendable as 93.22% claimed to practice the right hand wash times and 60.30% washed their hands correctly with soap and water while 37.69% washed with water only.
The sanitation aspects of environmental infrastructure as depicted by toilet availability and accessibility were also rated high in AMAC as respondents ascertained that faecal contact with humans was restricted and improved sanitation adhered to. From the study, 96.99% of the respondents indicated improved child stool disposal methods. Improved basic toilets were claimed to be available to 91.48% of respondents while 0.25% still practised open defecation. However, 72.68% of their toilet facilities were privately owned while 27.32% were shared. Similarly, in BAC, toilet availability and accessibility were also rated high as respondents ascertained that faecal contact with humans was minimal and improved sanitation adhered to. From the study, 82.16% of respondents indicated improved child stool disposal methods. Improved toilets were available to 76.88% of respondents while they further indicated no open defecation. However, 45.98% of their toilet facilities were privately owned while 53.52% were shared.
A statistically significant linear relationship (p<0.05) was deduced between the independent variables (occupation of mother/childminder and household wealth quintile) and the dependent variable (diarrhoea prevalence) in AMAC but no statistically significant linear relationship (p>0.05) was observed between the same variables in BAC (Table 3). In AMAC, a statistically significant linear relationship (p<0.05) between the independent variables (hand hygiene practices, child stool disposal method, type of toilet) and the dependent variable (diarrhoea prevalence) was observed (Table 4) but in BAC, a statistically significant linear relationship (p<0.05) was observed between the independent variables (water source for domestic use, time taken for a return trip, time spent on getting water and if water treatment was done) and the dependent variable (diarrhoea prevalence) (Table 5).
Variables |
Options | Frequency | Percent | X2 | df | p - value |
---|---|---|---|---|---|---|
Drinking Water Source | River/Stream | 14 | 3.5 | 7.929a | 12 | 0.791 |
Unsanitary Well | 15 | 3.75 | ||||
Sanitary Well/Borehole | 190 | 47.5 | ||||
Pipe borne tap | 45 | 11.25 | ||||
Bottle water | 13 | 3.25 | ||||
Sachet water | 115 | 28.75 | ||||
Water Source for Domestic Use | River/Stream | 15 | 3.75 | 4.323a | 8 | 0.827 |
Unsanitary Well | 57 | 14.25 | ||||
Sanitary Well/Borehole | 271 | 67.75 | ||||
Pipe borne tap | 57 | 14.25 | ||||
Water tank reservoir | 0 | 0 | ||||
Time Taken for A Return Trip | Less than 20 minutes/day | 182 | 45.5 | 15.514a | 8 | 0.05 |
20 to 30 minutes/day | 153 | 38.25 | ||||
>30 minutes to an hour/day | 55 | 13.75 | ||||
More than an hour a day | 8 | 2 | ||||
Never fetches water | 2 | 0.5 | ||||
Time Spent on Getting Water | Less than 20 minutes/day | 182 | 45.5 | 1.245a | 8 | 0.996 |
20 to 45 minutes/day | 153 | 38.25 | ||||
45 minutes to an hour/day | 55 | 13.75 | ||||
More than an hour a day | 8 | 2 | ||||
Never | 2 | 0.5 | ||||
Water Treatment Done? | Yes | 222 | 55.5 | 2.560a | 2 | 0.278 |
No | 177 | 44.25 | ||||
Hand wash with Water Only | Yes | 64 | 16 | 39.783a | 6 | 0 |
No | 240 | 60 | ||||
Not Really | 86 | 21.5 | ||||
Hand wash with Soap and Water | Yes | 278 | 69.5 | 79.539a | 4 | 0 |
No | 50 | 12.5 | ||||
Not Really | 47 | 11.75 | ||||
Hand Wash Time | Before Cooking | 250 | 62.5 | 33.547a | 12 | 0.001 |
After Cooking | 3 | 0.75 | ||||
Before Feeding Child | 1 | 0.25 | ||||
After Feeding Child | 1 | 0.25 | ||||
After Cleaning Child | 95 | 23.75 | ||||
Child's Stool Disposal | Burning/Burying | 12 | 3 | 26.552a | 8 | 0.001 |
Collected by a Garbage truck | 179 | 44.75 | ||||
Thrown into nearby bushes/river | 8 | 2 | ||||
Community dumpsite | 5 | 1.25 | ||||
Pour into toilet | 196 | 49 | ||||
Type of Toilet | Pit latrine with lid | 158 | 39.5 | 17.690a | 8 | 0.024 |
Pit latrine without lid | 33 | 8.25 | ||||
Pour Flush latrine | 83 | 20.75 | ||||
Water Cistern toilet | 125 | 31.25 | ||||
Open defecation | 1 | 0.25 | ||||
Toilet Ownership | Private | 290 | 72.68 | 3.512a | 6 | 0.742 |
Compound | 99 | 24.75 | ||||
Community | 4 | 1 | ||||
Public | 6 | 1.5 | ||||
None | 0 | 0 | ||||
Time Taken to Get to Toilet | Less than 15 minutes | 393 | 98.25 | 0.316a | 2 | 0.854 |
15 minutes to 30 minutes | 7 | 1.75 | ||||
Approximately 30 minutes | 0 | 0 | ||||
30 minutes to 1 hour | 0 | 0 | ||||
More than an hour | 0 | 0 |
Variables |
Options | Frequency | Percent | X2 | df | p – value |
---|---|---|---|---|---|---|
Drinking Water Source | River/Stream | 0 | 0 | 0.789a | 4 | 0.64 |
Unsanitary Well | 0 | 0 | ||||
Sanitary Well/Borehole | 210 | 53.03 | ||||
Pipe borne tap | 1 | 0.25 | ||||
Bottle water | 0 | 0 | ||||
Sachet water | 185 | 46.72 | ||||
Water Source for Domestic Use | River/Stream | 0 | 0 | 0.045a | 2 | 0.027 |
Unsanitary Well | 1 | 0.25 | ||||
Sanitary Well/Borehole | 395 | 99.75 | ||||
Pipe borne tap | 0 | 0 | ||||
Water tank reservoir | 0 | 0 | ||||
Time Taken for A Return Trip | Less than 20 minutes/day | 71 | 17.93 | 16.600a | 8 | 0.035 |
20 to 30 minutes/day | 198 | 50 | ||||
>30 minutes to an hour/day | 119 | 30.05 | ||||
More than an hour a day | 5 | 1.26 | ||||
Never fetches water | 3 | 0.76 | ||||
Time Spent on Getting Water | Less than 20 minutes/day | 47 | 11.87 | 16.600a | 8 | 0.035 |
20 to 45 minutes/day | 72 | 18.18 | ||||
45 minutes to an hour/day | 150 | 37.88 | ||||
More than an hour a day | 87 | 21.97 | ||||
Never | 40 | 10.1 | ||||
Water Treatment Done? | Yes | 2 | 0.51 | 15.099a | 2 | 0.001 |
No | 394 | 99.49 | ||||
Hand wash with Water Only | Yes | 64 | 16 | 6.192a | 8 | 0.626 |
No | 240 | 60 | ||||
Not Really | 86 | 21.5 | ||||
Hand wash with Soap and Water | Yes | 27 | 69.5 | 2.945a | 4 | 0.567 |
No | 50 | 12.5 | ||||
Not Really | 47 | 11.75 | ||||
Hand Wash Time | Before Cooking | 250 | 62.5 | 4.175a | 12 | 0.98 |
After Cooking | 3 | 0.75 | ||||
Before Feeding Child | 1 | 0.25 | ||||
After Feeding Child | 95 | 23.75 | ||||
After Cleaning Child | 22 | 5.5 | ||||
Child's Stool Disposal | Burning/Burying | 3 | 0.76 | 1.492a | 8 | 0.9093 |
Collected by a Garbage truck | 4 | 1.01 | ||||
Thrown into nearby bushes/river | 4 | 1.01 | ||||
Community dumpsite | 61 | 15.4 | ||||
Pour into toilet | 324 | 81.82 | ||||
Type of Toilet | Pit latrine with lid | 62 | 15.66 | |||
5.442a | 6 | 0.489 | ||||
Pit latrine without lid | 90 | 22.73 | ||||
Pour Flush latrine | 203 | 51.26 | ||||
Water Cistern toilet | 41 | 10.35 | ||||
Open defecation | 0 | 0 | ||||
Toilet Ownership | Private | 183 | 46.21 | 0.945a | 4 | 0.918 |
Compound | 209 | 52.78 | ||||
Community | 4 | 1.01 | ||||
Public | 0 | 0 | ||||
None | 0 | 0 | ||||
Time Taken to Get to Toilet | Less than 15 minutes | 391 | 98.74 | 0.182a | 2 | 0.913 |
15 minutes to 30 minutes | 4 | 1.01 | ||||
Approximately 30 minutes | 0 | 0 | ||||
30 minutes to 1 hour | 0 | 0 | ||||
More than an hour | 0 | 0 |
Discussion
This study captured the environmental infrastructure available in two suburban districts (AMAC and BAC) of Abuja, Federal Capital Territory of Nigeria and their relationship with diarrhoea occurrence in under-five years old in the area.
This study shows that diarrhoea occurrence is only affected by the occupation of the mother or childminder and the wealth quintile of the family in AMAC, while in BAC, none of the socio-demographic or socio-economic factors was associated with diarrhoea occurrence. This could be attributable to notable differences in the occupational and wealth status of respondents in AMAC which could affect their allocation of finances to issues of hygiene and sanitation. The same cannot be said for BAC respondents who were within the same financial capabilities. This is in agreement with the works by (Kumi-Kyereme et al.,2015) and (Hunachew et al., 2018) that affirmed that household wealth plays a major role in child mortality from diarrhoea.
However, in contrast, (Usman et al., 2009) believed that children from mothers in occupations especially within the informal sector like farming had higher odds of diarrhoea.
Since a higher percentage of the study populations in AMAC and BAC had access to limited water services, which refers to improved water sources but not safely managed, their exposure to non-potable water is high. Interestingly, the drinking water source as a variable was not statistically significant. This can be attributed to the fact that the respondents mostly alluded to treating their drinking water before use which invariably will curtail the exposure of under-fives to enteric bacteria. This agrees with the studies of (Bain et al., 2021) which suggest that half of the population of Nigeria is exposed to high-risk drinking water at the point of use. Furthermore, the study by (Akinyemi et al., 2019) corroborates this assertion and also affirmed that the wealth quintile remains a factor for households’ engagement in the treatment of water.
On sanitation variables, the study areas were shown to have improved sanitation facilities. Their improved child stool disposal methods and basic improved toilet types ensure no human and faeces contact. For toilet ownership, AMAC had more privately owned toilets while BAC had more shared toilets. Expectedly, there will be a remarkable reduction in the dangers associated with open defecation for both areas but the intrinsic sanitation management of shared toilets remains a factor to be dealt with. However, child’s stool disposal remained statistically significant in AMAC and could be attributed to the fact that though improved and basic toilet facilities abound, there was a large occurrence of dilapidated broken sewers with the sullage being discharged directly into the streets and soils. Also, one cannot ignore the dangers posed by disposing of stool-soiled diapers in the garbage trucks/dumpsites which are mostly unprotected from pets, like dogs. These pets scavenge and take the waste back again to homes where there are no dog pens. This is in agreement with the studies of (Gebru et al., 2014) on accessible and improved sanitation on diarrhoea prevalence.
It was also noted that the type of toilet was statistically significant in AMAC despite the improved but limited toilet types that abound in the study area. This is also attributable to the large occurrence of dilapidated broken sewers and their attendant health risks to the inhabitants. This was noted in the work of (Cameron, 2009). However, the findings of (Engell, 2013) showed no significant difference in the type of toilet and diarrhoea occurrence in households.
The study area was low on hand hygiene practices as most of the respondents indicated practising hand washing only before cooking and after cleaning the child indicating that they are not very aware of the United Nations global hand washing moments despite knowing rightly to wash hands with soap and water. Hence, it was statistically significant in the study. This finding corroborates the study of (Oloruntoba et al., 2014) that concluded that proper hand hygiene at critical times is a major factor for diarrhoea curtailment. This study established that diarrhoea risk factors are community specific as shown in the work of (Fagbamigbe et al., 2017).
The effects of the availability of infrastructure on diarrhoea occurrence among children under-five years in Abuja, the Federal Capital Territory require urgent attention. The interventions need to be implemented immediately given that climate change is gradually interrupting water systems. This further impedes health especially as the female folks that bear the brunt of WASH, are stuck in making choices between climate change and sanitation. Our study suggests the urgent need to improve the environmental infrastructure of the FCT, Nigeria. Human and faecal contact must be reduced to the barest minimum by the increased provision of safely managed sanitation services (improved toilets) and encouraging households on their proper use and maintenance. Also, there is the need to sensitize and engage mothers/childminders on environmental, hygiene and sanitation practices. The study has further shown that the involvement of mothers and childminders in programs and policy designs is critical to the success of hand hygiene interventions in alleviating diarrhoea and the global burden of disease in Africa.
The authors are grateful to the Area Councils’ Environmental Health and Primary Health Care Units of the Federal Capital Territory Administration’s Health and Human Services Secretariat for the support. The authors appreciate individuals who were of tremendous help in the course of this study as they provided insights and comments that assisted in the study.
INFORMED CONSENT FROM PARTICIPANTS
All participants were provided written informed consent which they signed up for before the administration of the questionnaire. Participation was voluntary, and confidentiality was assured.
DATA AVAILABILITY STATEMENT
The authors confirm that the data supporting the findings of this study are captured in the manuscript.
DECLARATION OF COMPETING INTERESTS
The authors have no competing interests.
LIST OF ABBREVIATIONS
AMAC ABUJA MUNICIPAL AREA COUNCIL
BAC BWARI AREA COUNCIL
WHO WORLD HEALTH ORGANISATION
WASH WATER, SANITATION AND HYGIENE
FCT FEDERAL CAPITAL TERRITORY
NGN NIGERIAN NAIRA
df DEGREES OF FREEDOM
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref
Indexed at, Google Scholar, Crossref